CN105417593B - A kind of eutrophic lake deposit in-situ passivation technology - Google Patents
A kind of eutrophic lake deposit in-situ passivation technology Download PDFInfo
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- CN105417593B CN105417593B CN201510823659.1A CN201510823659A CN105417593B CN 105417593 B CN105417593 B CN 105417593B CN 201510823659 A CN201510823659 A CN 201510823659A CN 105417593 B CN105417593 B CN 105417593B
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
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- Environmental & Geological Engineering (AREA)
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Abstract
The invention discloses a kind of eutrophic lake deposit in-situ passivation technology, preparation method including passivator, passivator field adds and passivator field trial, compared with prior art, the present invention adds passivator by cutting off the backward polluted water region of external source pollution, nutritive salt in passivator adsorbed water body and deposit, simultaneously passivation layer is formed on deposit top layer, pass through adsorption, ion exchange, the effects such as physical barrier reduce nutriment and supplied to overlying water, so as to reach the purpose of control body eutrophication, made with material simple, cost is cheap, field is easy to implement, repairing effect is obvious, it is applied widely, to aquatile nonhazardous, the features such as non-secondary pollution, overcome the deficiencies in the prior art, with the value promoted the use of.
Description
Technical field
The present invention relates to a kind of green technology, more particularly to a kind of eutrophic lake deposit in-situ passivation technology.
Background technology
Water body in lake eutrophication is on the rise, and has become current main Environmental Problems urgently to be resolved hurrily.Lake Fu Ying
The generation of fosterization and water body the content of nitrogen and phosphorous are closely related.Water body in lake nitrogen, the existing external source import in phosphorus source, also there is internal loading,
After external source import is progressively effectively controlled, the compound fertilizer discharged from bed mud can still result in lake eutrophication.
Under the conditions of strict external source contamination control, due to the sustained release of deposit endogenous pollution, lake water water quality obtains substantially
Improvement generally requires many decades.Therefore, internal loading is controlled to turn into the key for administering lake eutrophication.
Bottom mud in lake pollution control technology mainly has in-situ treatment and dystopy to handle two classes.In-situ treatment technology refers to dirt
Dye bed mud stay put, using physics, chemistry, biology method reduce pollutant load and prevent pollutant from sediment release to
In water body, dystopy treatment technology refers to dig out polluted bed mud and be transported to reprocess elsewhere, prevents its polluted-water.Mesh
Preceding wide variety of in-situ treatment technology both at home and abroad mainly has original position covering, in-situ passivation, biological prosthetic etc., dystopy treatment technology
Mainly including Technology for Environmental Dredging of Contaminated Bottom Silt etc..
Original position, which covers, can produce some environmental problems, and first, the pollutant after covering remains in original place, and barriering effect is held
Long property and the lasting effect of coating are closely related；Second, covering easily occurs mixed with polluted bed mud when covering and constructing, made
Discharged into polluted bed mud gap water pollutant and diffuse to overlying water, cause secondary pollution；3rd, covering substitutes original bottom
Mud, destroy ECOLOGY OF BENTHOS IN environment；4th, covering is vulnerable to current, stormy waves and benthic disturbance, reduces barrier effect
Fruit.
There are some drawbacks in bioremediation technology, in implementation process because plant growth needs the conditions such as illumination, water body
The size of depth will directly affect biological prosthetic effect, and therefore, phytoremediation technology generally also can only be in shallow water type lake
Significant results can be obtained.
The shortcomings that Sediment Dredging, is as follows：First, because the strand suction disturbance for dredging ship twisting sucker head can cause thin during digging
The suspension and diffusion of grain thing, while slurry transportation process also easily causes the pollution of surrounding environment；Second, to dredging technology requirement
Very high, dredging is too shallow can not effectively to remove polluter, and dredging is too deep both devastatingly to have changed lakebed form and bottom is dwelt aquatic life
Substance environment, weakening the buffer capacity after the input of bottom mud in lake exogenous pollutant again, the restoration of the ecosystem to the later stage is more difficult,
Dredge it is improper only endogenous pollution load can be made to obtain a certain degree of suppression in a short time, with particle settles, energetic disturbance and
The continuous action of the biogeochemical processes such as bioconversion, endogenous reply phenomenon would be possible to progressively occur, or even water occurs
Matter is than situation about deteriorating before dredging.3rd, Sediment Dredging can produce substantial amounts of mud needs while reducing sediment pollution thing
Further processing, polluted bed mud, which is dealt with improperly, can more cause secondary pollution.4th, Sediment Dredging is costly, Dredging Process
Substantial contribution input is both needed to polluted bed mud post-processing；5th, Sediment Dredging receives the limitation of water depth, at present bed mud ring
Protect dredging to substantially reduce with the lake region dredging efficiency of headwater depth in 15m, it is difficult to implement.
The content of the invention
The purpose of the present invention is that to provide a kind of eutrophic lake deposit original position to solve the above problems blunt
Change technology.
The present invention is achieved through the following technical solutions above-mentioned purpose：
The present invention includes the preparation method of passivator, passivator field add with passivator field trial,
The preparation method of the passivator：Its composition includes aluminum sulfate, clay and stone flour, compares aluminum sulfate according to quality：It is glutinous
Soil：Stone flour is 30:15:55 mixing, stir, and then plus mud is made in water, is transferred to granulating disc, is processed into particle diameter about
For 2-3mm spheric granules, then dry through high temperature；
Passivator field adds：By transport after the good passivator pack of above-mentioned production to waters to be repaired, broadcast with particulate matter
Spread machine or spades is equably added to designated area, passivator is settled down to rapidly lakebed, and deposit surface is covered in after cracking, blunt
Agent dosage is 350~400g/m2；
Passivator field trial：About 20 mu of passivation field trial region is chosen, adds about 5t passivator in passivation region altogether, it is blunt
Agent is used in test block before adding and lays enclosure, simulates under cut-out external source pollution input condition, verifies repairing effect.
Specifically, the stone flour is carbonatite powder；Aluminum sulfate, clay and stone flour are the mesh powder of particle diameter 100.
The beneficial effects of the present invention are：
The present invention is a kind of eutrophic lake deposit in-situ passivation technology, and compared with prior art, the present invention passes through
Cut-out external source pollutes backward polluted water region and adds passivator, the nutritive salt in passivator adsorbed water body and deposit, while heavy
Product thing top layer forms passivation layer, and nutriment is reduced to overlying water by effects such as adsorption, ion exchange, physical barriers
Supply, so as to reach the purpose of control body eutrophication, there is material to make simple, cost is cheap, and field is easy to implement, repaiies
Multiple positive effect, it is applied widely, to aquatile nonhazardous, the features such as non-secondary pollution, overcome prior art not
Foot, there is the value promoted the use of.
Brief description of the drawings
Fig. 1 is passivation region of the present invention and check plot water body NH3-N (left side) and TP (right side) changes of contents comparison diagram；
Fig. 2 is passivation region and check plot water body DO content balance figures；
Fig. 3 is passivation region and check plot sediment water interface Dissolved reactive phosphorus (SRP) content balance figure.
Embodiment
The invention will be further described below in conjunction with the accompanying drawings：
The present invention includes the preparation method of passivator, passivator field add with passivator field trial,
The preparation method of the passivator：Its composition includes aluminum sulfate, clay and stone flour, compares aluminum sulfate according to quality：It is glutinous
Soil：Stone flour is 30:15:55 mixing, stir, and then plus mud is made in water, is transferred to granulating disc, is processed into particle diameter about
For 2-3mm spheric granules, then dry through high temperature；
Passivator field adds：By transport after the good passivator pack of above-mentioned production to area to be repaired, broadcast with particulate matter
Spread machine or spades is equably added to designated area, passivator is settled down to rapidly lakebed, and deposit surface is covered in after cracking, blunt
Agent optimum dosage is 350~400g/m2；
Passivator field trial：About 20 mu of passivation field trial region is chosen, adds about 5t passivator in passivation region altogether, it is blunt
Agent is used in test block before adding and lays enclosure, simulates under cut-out external source pollution input condition, verifies repairing effect.
Specifically, the stone flour is carbonatite powder；Aluminum sulfate, clay and stone flour are the mesh powder of particle diameter 100.
Experiment effect is described as follows：
1 year post-passivation area water body NH is implemented in passivation3- N content is 0.23mg/L, check plot 0.80mg/L, passivation region water
Body total phosphorus (TP) content is 0.03mg/L, check plot 0.13mg/L.Passivation region water body NH3- N and TP belongs to surface water II categories
Standard, and check plot is V classes.Passivation implements post-passivation area NH3-N and TP content and is below check plot of the same period, passivation region water body
Nutrient concentrations reduce degree and are significantly greater than check plot (as shown in Figure 1).After passivator adds 1 year, passivation region water body NH3-N
It is respectively the 29% and 23% of check plot with TP contents.Due to the input that passivation region pollutes without external source, the passivator added is not only
Adsorbed water body nutritive salt, passivation layer also is formed in deposit surface, significantly reduces nutritive salt internal loading amount and passivation region
Water/sediment interface is oxygen-enriched state, reduces Inner nutrition salt burst size.It is gradually extensive as passivation region water quality gradually improves
Multiple submerged plant can also slow down stormy waves, fixed bed mud, greatly strengthen self-purification of waters, reduce water body ammonia nitrogen, the product of phosphorus
It is tired, therefore passivation region water nutrition salt content is significantly lower than check plot.
Passivation implements 1 year post-passivation area water body and recovers normal from the anaerobic condition before passivation, and check plot is still anoxic shape
State, passivator are obvious to oxygen content of water repairing effect.Passivator adds 1 year post-passivation area and contained with check plot DO as shown in Figure 2
Amount difference is obvious, and passivation region water column DO average values are 9.39mg/L, is 5.8 times of check plot (1.63mg/L).Passivation region is different
Depth water body DO contents are all higher than 9mg/L, and wherein top layer 0.5m is 9.77mg/L, bottom 9.09mg/L, far above check plot
(top layer 2.21mg/L, bottom 1.22mg/L).
Sediment Pore Water is the main medium that mass exchange occurs between deposit and overlying water.Sediment phosphorus discharges
Pore water is initially entered, and then is spread to upper layer sediment-water termination and overlying water mixing.As shown in figure 3, Dissolved reactive phosphorus
(SRP) concentration shows as lake water on vertical<Overlying water<Pore water.Two lake water sample SRP contents of passivation region are respectively
0.02mg/L and 0.03mg/L, check plot lake water SRP contents are 0.13mg/L, about the 5 of passivation region times.Two depositions of passivation region
The SRP contents of thing post core overlying water are respectively 0.09mg/L and 0.12mg/L, and the SRP contents of check plot overlying water are 0.25mg/
2.5 times of L, about passivation region.Column core of sediments 0-2cm pore water SRP contents are respectively 0.72mg/L and 1.46mg/L, remote small
In check plot (3.63mg/L).The following pore water SRP contents of passivation region column core of sediments 2cm and check plot Sediment Pore Water are poor
It is not little.Passivation region deposit hole post core pore water SRP contents slightly reduce from top layer to 10cm, and check plot column core of sediments
Pore water SRP contents are maximum in 0-2cm, far above below 2cm pore waters (average value 0.83mg/L).Therefore, add
Passivator the release of Phosphorus in Sediments is effectively inhibited by effects such as adsorption, ion exchanges, especially 0-2cm is deposited
Thing inhibitory action is most obvious.
The general principle and principal character and advantages of the present invention of the present invention has been shown and described above.The technology of the industry
Personnel are it should be appreciated that the present invention is not limited to the above embodiments, and the simply explanation described in above-described embodiment and specification is originally
The principle of invention, without departing from the spirit and scope of the present invention, various changes and modifications of the present invention are possible, these changes
Change and improvement all fall within the protetion scope of the claimed invention.The claimed scope of the invention by appended claims and its
Equivalent thereof.
Claims (3)
- A kind of 1. eutrophic lake deposit in-situ passivation method, it is characterised in that：Preparation method including passivator, passivation Agent field add with passivator field trial,The preparation method of the passivator：Its composition includes aluminum sulfate, clay and stone flour, compares aluminum sulfate according to quality：Clay：Stone Powder is 30:15:55 mixing, stir, and then plus mud is made in water, is transferred to granulating disc, and it is 2mm's to be processed into particle diameter Spheric granules, then dried through high temperature；Passivator field adds：By transport after the good passivator pack of above-mentioned production to waters to be repaired, with particulate matter planting machine Or spades is equably added to designated area, passivator is settled down to rapidly lakebed, deposit surface, passivator is covered in after cracking Dosage is 350~400g/m2；Passivator field trial：20 mu of passivation field trial region is chosen, adds 5t passivator in passivation region altogether, passivator adds It is preceding to lay enclosure in test block, simulate under cut-out external source pollution input condition, verify repairing effect.
- 2. eutrophic lake deposit in-situ passivation method according to claim 1, it is characterised in that：The stone flour is Carbonatite powder.
- 3. eutrophic lake deposit in-situ passivation method according to claim 1, it is characterised in that：Aluminum sulfate, stick Soil and stone flour are the mesh powder of particle diameter 100.
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| CN107382026A (en) * | 2017-07-19 | 2017-11-24 | 南京必蓝环境技术有限公司 | A kind of method for improveing riverbed bed mud and the method for configuring riverbed bed mud modifying agent |
| CN112607956A (en) * | 2020-11-25 | 2021-04-06 | 中国科学院地球化学研究所 | Ecological restoration and aquatic ecosystem restoration method for polluted water body of plateau lake |
Citations (3)
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| US20110247985A1 (en) * | 2004-08-26 | 2011-10-13 | Earth Renaissance Technologies, Llc | Hybrid chemical/mechanical method and apparatus for inactivating and removing pharmaceuticals and other contaminants from water |
| CN102557221A (en) * | 2012-02-15 | 2012-07-11 | 中国科学院地球化学研究所 | Preparation method and application of eutrophic water body sediment phosphor in-situ passivating agent |
| CN104876410A (en) * | 2015-04-29 | 2015-09-02 | 暨南大学 | In-situ continuous remediation method for heavy metals and/or nitrogen and phosphorus polluted bottom mud |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS6014990A (en) * | 1983-07-05 | 1985-01-25 | Kurita Water Ind Ltd | Dephosphorization process |
| CN102399045A (en) * | 2010-09-13 | 2012-04-04 | 清华大学 | Composite medicament for fixing nitrogen and phosphorous in riverbed sludge, and preparation and application method thereof |
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Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20110247985A1 (en) * | 2004-08-26 | 2011-10-13 | Earth Renaissance Technologies, Llc | Hybrid chemical/mechanical method and apparatus for inactivating and removing pharmaceuticals and other contaminants from water |
| CN102557221A (en) * | 2012-02-15 | 2012-07-11 | 中国科学院地球化学研究所 | Preparation method and application of eutrophic water body sediment phosphor in-situ passivating agent |
| CN104876410A (en) * | 2015-04-29 | 2015-09-02 | 暨南大学 | In-situ continuous remediation method for heavy metals and/or nitrogen and phosphorus polluted bottom mud |
Non-Patent Citations (1)
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| "沉积物磷原位钝化技术研究进展";杨永琼等;《地球科学进展》;20130630;第28卷(第6期);第676-680页 * |
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